This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. 7~fRASER Euwz~~ ';fJIte4t , , , , tt41f1~ ad /ltm4 by L. D. Love, Forester 1 In 1937 the Fraser Experimental Forest was established in the heart of the Central Rocky Mountains near the Continental Divide 65 miles north and west of Denver. This 36-squaremile outdoor research laboratory is well suited for the study of pressing problems related to water yield from high-elevation forests and alpine areas. Here in the West, water is a basic resource. It is necessary to the life and livelihood of our people, hence the source of supply is vitally important to all of us. In Colorado the annual yield from the Central Rocky Mountains is about 20 million acre ..feet. Eighty-five percent of this water comes from alpine areas and mountain forests. Each acre yields at least I acre -foot of water a year, enough to supply the needs of five families. The relation between the sources in the high country, the elaborate transmountain diversion systems. and the users in the cities and on the irrigated farms is shown by this schematic helicopter view of the countryside surrounding the Fraser Experimental Forest. Here, we see the vast Colorado-Big Thompson transmountain diversion that taps the headwaters of the colorado River and brings its water through a tunnel ;9-3/4 feet in diameter and 13 miles long under the Continental Divide to far-off users in eastern Colorado. Also, we see the Fraser River transmountain diversion constructed by the City of Dentrer This diversion passes through the Continental Divide via the pioneer bore of the 6-mile Moffat Tunnel. to bring in water from St. Louis and Vasquez Creeks. Rocky Mountain Forest and Range Experiment Station, Forest Service, U. S. Department of Agriculture, with headquarters at Fort Collins, Colorado, in cooperation with Colorado State University. 1 Three-fourths of the experimental £0 res t lie s above 1 0, Z 5 0 feet. Elevation of Byers Peak, the highest point in the forest, is IZ,804 feet. Water from much of this area is diverted to the City of Denver. tD·· .-:4 ,.. '. ~. A I I o MILE S / fxperimen- fal plot Skyline crone f)enver WfJtel' diversion I food The climate is cool, with an average yearly temperatur.e of 35°F. Mean monthly temperature for January is 15°F.; for July, 55°F. Growing season is about 75 days; the frostfree period is from mid-June to mid-September. Annual precipitation, two-thirds of which falls as snow, varies from 15 to 30 inches, with an average of Z4 inches. ~ -ts:: r SNOW P~RIOD RAIN ~RIOD SNOW P!;R100 4 0 '-' 60 f .2 40 Q. 20 80 LL -=:; s:: o r-3 :E r-2r- - r- '0. '0 r-I ~ ~ E ~ 0. M A M J J A SON D MONTHLY PRt:CIPITATION J ~ Lodgepole pine, Engelmann spruce, and subalpine fir are the important tree species. In virgin stands they commonly reach ages of ZOO to 400 years. Quaking aspen grows in the openings left by fire and logging. The forest floor is covered with deep litter and often dense mats of grouse whortleberry. Young pine, spruce, and fir, along with scattered as pe n and buffaloberry, also grow beneath the forest canopy. Higher in the alpine areas barren rocks intermix with meadows containing ·grasses, . sedges, weeds, and dwarf willows. _ Lodgepole Pine WaWr.41 ~nge'mann '",..l i N " Alpine M~AN MAXIMUM~IIII ~ II~M~J~UM II M A M J MONTHLY J A SON D HMP~RATURt Most of the research at Fraser is concentrated on watershed management to improve and increase our supply of water. Records show that half of the annual precipitation on the forest becomes streamflow. This amounts to a water yield of Ito 1.5 acre -feet per acre. About 70 percent of this yield comes from melting snow during April, May, and JUne. Snowpacks and surrounding forest areas have been understudy since 1937. First came observations in natural stands to see how forest types and canopy patterns affect snow accumulation. Next came plot studies of thinnings and harvest cuttings, and measurements to determine effects of winter accumulation of snow, spring snowfall and rate of snowmelt, summer precipitation, and evapo-transpiration of soil moisture. The final step in this logical:sequence was to apply these systems of timber harvesting to whole watersheds then measure the effect on strealllfiow. Effects of timber harvest on water yields are being studied on this pair of watersheds at the Fraser Experdmental Forest The following explanations, photographs, and diagraxns will show briefly the results of our experixnents during the past quarter-century. Early studies showed that less precipitation reached the ground under dense stands of lodgepole pine than under aspen and grassland. These studies were intended to give clues as to the effects that would be produced when forest stands were harvested for tixnber or thinned to stixnulate tree growth. IN J:LU (; NCI; OJ: THR~~ [Ii SOURCI;; 01= WAT~R STORAG~ SPRING PR EC tPI TAT JON SUMM~12. PR(;CI PITATI ON ~ QUAK1NG ~~ TYP(;S ~\'\Jfnk S GR ND -----------i~es of water---------- WJNTI;R. SNOW \~ VI;G~TATIONAL Twenty 5-acre harvestcutting plots for forest and watershed management res ear c h were laid out in mature lodgepole pine in 1938. In 1940, the plots were logged, ranging from a clear cut of all trees larger than 9.5 inches in diameter to an uncut virgin area. (See map. } I , I f' ' /I , ' ~----- I I ",/ .... ", .... / I I ( \ \ I - 1 ........ ...."~ " ( [ , ..... //1 , ............ 1J , (I " \ OHf 0 , \/ 1 /o I / I " ~: " V / ,..---...--. 1/ I \ I "~ I~ I"'-..J I I ""',.IV) / I I ,/ "'------..... " \ \ , I \ \ ,, I \ \\ I\ I I I I I LODG~POL~ PINE' HAlV~ST CUTTING PLOTS SCAL~ o 10 20 chains (1/4 mile) ..... 1 _ _ _..L-_ _----l, ------ Road L~G~ND I2.{;S~JtV~ STAN • Virgin 6 M hm. per ~ 4M hm.per liBl Will' D 2 M hrn. pet Commercial cut 4 Mter tr e e s are re" moved in timber harvesting. more of the winter snow can reach the ground. Here, less of its water content is lost to the air. and so more is available for streamflow. From the I 0 d g e pol e pine plots an increase in water available for str eamflow was as shown here. MATURE LODGEPOLE PINE INFLUENCE OF CUTTING ON WATER YIELD ~ESERVE VOLUME..!.! "",",TER AVAILABLE -"0 4 Inches of Watet'" Board Feet Per Acre- · STREAMFLOW Percent. mcreOM 31 j[l~52 ,m:2.44 i 20 ~~i'9 .t 11 .3a i 10 I .1IQ34! 0 -!. In tr""1tes to inch. . d.b.h. and k:I~ MATURE LODGEPOLE PINE INFLUENCE OF CUTTING ON GROWTH ~ MORTALITY RESERVE VOWME.lI Bocwd Feet Per Acre NONE ('>It.) GROWTH.&I MO>=lTALITY Boc:u'd F1Itet Per Ac..-e +36 I 1 0 I -45 1103 1 I~ I -46 I 125 ~y 1 I I ",; 1 +16 I I 1 88 . V ~ +30 174 I .itApproximatetw 9in'II CIf rnof-'taU'ty pIots- WCIS wincifciir. 01"1 t:recrWd Growth and mortality of the residual stand were also measured. Mortality exceeded growth on all of the cut plots except those cleared of all saw-Iog-sized trees. Principal cause of mortality was windthrow. This result, together with that from the hydrologic measurements, led to the conclusion that clear cutting of mature lodgepole pine is the most desirable method of harvesting. In 1944 an experim.ent to' determ.ine the best m.ethO'd O'f harvesting spruce-fir was started. The study cO'nsists O'f fO'ur 8-acre plO'ts, three O'f which were treated differently and the fO'urth left as an uncut contrO'l. The. treatm.ents used are alternate -strip clear cutting. grO'up-selectiO'n cutting, and single-tree selectiO'n cuttIng. In each plO't 60 percent O'f the vO'lum.e· O'f tim.ber was rem.O'ved. Alternate~strip clear cutting rem.O'ved 50 pEil"cent O'fthe volum.e by cutting all trees larger than 9.5 inches in diam.eter in alternate strips; an additional 10 percent was rem.O'ved frO'm. the rem.aining area by cutting O'verm.ature ttrees. Dam.age to' reprO'ductiO'n was m.O'derate O'n the cut strips. GrO'up-selectiO'n cutting rem.O'ved.50 percent O'f the volum.e by cutting all trees larger than 9.5 inches in diam.eter in sm.all circular clear-cut grO'ups; an additiO'nal 10 percent was rem.oved frO'm. the rem.aining area by cutting O'verm.ature trees. Dam.age to' reprO'ductiO'n was .light in the O'penings. Single-tree selectiO'n cutting rem.O'ved 60 percent O'f the vO'lum.e by cutting unifO'rm.ly O'ver the plO't. NO' trees sm.aller than 9.5 inches in diam.eter were rem.O'ved. Dam.age to' reprO'duction was heavy O'n the plO't. SNOW STORAGE SnO'wfall reaching the grO'und increased after harvest cuttings in the spruce -fir plots. Measurem.ents in fO'ur O'f the years since lO'gging shO'W that the cut plO'ts have stO'red an average O'f 22 percent m.O're water than the uncut. NO' significant difference in snO'w accum.ulatiO'n results frO'm. variatiO'n in cutting. In all three~ m.ethO'ds. 60 percent O'f the vO'lum.e was rem.O'ved; O'nly the pattern varied. OLD ...... GROWTH SPRUCEr-FIR INFLUENCE 0,. HARVESTING METHODS ~SNON STORAGE Percent Increase ·~14.9 ~ fPS.3 I 1 20.1 I J t I r 23.4 I I ]t""153 i23 4 it12.41 0 SNOWMELT Weekly mea~urements during the spring showed only slight differences in the rates of melt. Snow melted at the slowe st rate in the uncut plot.. Effects of the different cutting methods showed: Alternate strip Group selection Single tree Uncut Melt 'water per day (inches) GROWTH 0.34 AND 0.31 0.36 0.28 MORTALITY Growth and mortality were also measured. These two factors as well as snowmelt were slightly more favorable under the group-selection pattern. However, because of the difficulty of applying the method, alternate-strip clear cutting was chosen for watershed studies at the experimental forest. OLD-GROWTH SPRUCE-F"IR INFLUENCE OF CUTTING ON GROWTH 6. MORTAUTY GI=lOWTH MO~ALlTY Board Feet Per Acye 28 70 ~l/ 46 61 ~!I 43 69 ~ 116 72 1.1 2/3tdi of mortality was windfall ~ 9/lO!ht of mortalitlJ wos windfall REGENERATION '*.Jtl Lodgepole pine • Regeneration is usually adequate. Prior to. cutting, the spruce-fir plots contained 6. 344 seedlings and saplings per acre. Logging destroyed 52 percent. Subsequent reproduction raised the count to 4,809. per acre 5 years after logging. The new seedlings are composed of a higher ratio of spruce and some lodgepole pine, indicating that cutting favors these species over subalpine fir. t:ngeimann spruce I. ,.,.,..,...... WE] Su~alpjn~ GR.OUP fir SElEcnON Two methods of thinning dense stands of 35-year-old lodgepole pine were used to study the effects on snow storage. On six3/4-acre plots. single-tree thinning left 630 of the better trees per acre spaced 8.5 feet apart. On six other plots, crop-tree thinning consisted of cutting all trees in a 16-foot diameter circle around each of 100 of the best developed trees per acre. No thinning wa.s done on six other plots. Snow storage was measured on;all 18 plots. Here are the results: YOUNG LODGEPOLE PINE INFWENCE ol"THINNING 0" SNOW STORAGE Inches o'f Werter Percent Increase 1i~12.34! 23.0 I '==: I M'<rr.72 ·' ft ll~ i 168 I I I • . I ,.-ZIO.03j 0 NOTE: ....... Each tree s\:jmbol represents 500 trees. In 1949 the rates of snowmelt on these plots were as follows: Melt water per day (inches) YOUNG LODGEPOLE ~--- Single -tree Crop-tree Unthinned 0.38 0.36 0.26 PINE INFLUENCE ol"THINNING 0" AVERAGE ANNUAL DIAMETER GROWTH o"'SELECTED TREES __-~WERAGE ANNUAL DIAMETER GROWTH'\. 8 YEARS I3EF()R£THINNING AVERAGE· ANNUAL DIAMETER GROWTH~8 YEARS AFTEf:< CROP....TREE THINNING NONE Intensive competition for growing space does not permit good development in the de.nse young stands. of 1 0 d g e pol e pine that, normally 0 c cur afte r clear cutting or fire. Lodgepole pine, although intolerant. does not thin • well naturally. S eve r e crowding of young trees of the same size results in retarded diarneter and i height growth; therefore art i f i cia 1 thinningi s needed. , , , ., Cutting timber on small experimental plots has resulted in the accumulation of greater amounts of water, mostly from added volumes of snow. Presumably this water will cause increased streamflow. The assumption is still problematical, however, until similar cutting is done in a forested watershed from which streamflow can be measured. A watershed study has been started to provide the answer. FOOL CREEK WATERSHED EAST ST. LOUIS CREEK WATERSHED Fool Creek watershed, a 7l4-acre drainage, was selected for this study. Streamflow, rainfall, and snow storage have been measured since 1940. Average annual yield of water in streamflow would cover the watershed to a depth of 13 inches. Elevations range from 9,500 to 11,500 feet. About half the 6 million board feet of timber is lodgepole pine and the rest is a mixture of Engelmann spruce and subalpine fir. East St. Lou i s Creek is the companion watershed to Fool Creek. It will not be logged. Since 1943 streamflow and snow storage have been measured on this 1,984acre drainage. Elevations range from 9,500 to 12,000 feet; the vegetation consists of lodgepole pine, Engelmann spruce, sub. alpine fir. and alpine turf above timberline. Annual water yield is equivalent to an 18inch depth over the area. The flow from the two experimental watersheds is well correlated and procedures are available to estimate the flow of Fool Creek from that of East St. Louis Creek. Streamflow is the quantity of surface water flowing past a given point in a stream channel and is measured by means of flumes, weirs, or stabilized channels. It is related to the cros s -sectional area .of the flume, weir, or channel, and to the velocity of the flowing water. Streamflow is expressed as a rate in cubic feet per second, or as an amount in acre-~eet; or inches depth over a known area. At Fool Creek the gaging station is a combination of a flume and two broadcre sted wei r s. Streamflow shown here is from snowmelt; water is flowing at the rate of 13 cubic feet per second. To harvest the timber on Fool Creek watershed, roads (3.3 miles of main access and 8. 6 miles of spur) were built in 1950 and 1951. Timber harvest began in 1954 and ended in 1956. Alternate clear-cut strips extending up and down slopes are bounded at the ends by contour roads. Four widths of strip were used: 1, 2, 3, and 6 chains. The slope length of most strips is about 600 feet, the slope distance between spur roads. To minimize damage to the stream course, no timber was cut within 90 feet of the main stream. On the strips designated for cutting, all live trees 4 inches d. b. h. and larger were felled. The tops were lopped and scattered. Merchantable forest covered 550 acres of the total 714 acres in the watershed, with 55 percent in the lodgepole pine type and 45 percent-in the spruce -fir type. The stand was 250 to 300 years old. Watershed area cleared was 278 acres. This includes 35 acres in road system and 243 acres of c 1 ear - cut strips, which yielded 3,560 M b. m. of timber in the following products: M b.m. Saw logs Poles Posts Pulp - 12 - 2, .200 1,000 60 300 Percent 62 28 2 8 o~a5t Sf. louis I The analysis to deter:rnine the effect of thetreat:rnent on water yield consists of e sti:rnating what the yield of Fool Creek would have been if there had been no treat:rnent, and co:rnparing this esti:rnated value with that recorded. The watershed of East St. Louis Creek has not been disturbed by ti:rnber harvest, and so re:rnains as a "control" with its strea:rnflow reflecting only the natural annual variations in cli:rnate. ~ool Creek 8 Acre-feet 1957 1958 1959 254 200 125 186 714 acres 1943-54 6 4 2 o~~~~~~~~ 8 1956 The esti:rnated increase in water yield fro:rn the Fool Creek watershed was 1956 CYeek 1984 acres The study was not designed to deter:rnine the effect of ti:rn..;, ber harvest and its acco:rnpanying road syste:rn on sedi:rnent yield. However, to confir:rn the belief that erosion would not be a prob1e:rn, a sedi:rnent basin was constructed in 1951 i:rn:rnediately below the strea:rn-gaging station. Sedi:rnent yield has been low and is correlated with discharge. Because :rneasure:rnents were begun after the road syste:rn was constructed, no conclusions can be draWn as to the effect of the watershed treat:rnent on sedi:rne.ntyield. However, the annual sedi:rnent yield fro:rnthe watershed following logging averaged only 1 •. 5 cubic feet per a,cre, wet volu:rne. 1958 2 o~~~~~u-.u 8 __ 1959 6 MAY JUNE JULY AUG .SEPT Pond of 1/4 acrefoot capacity in which to trap sediment 01. At the end of winter the entire forest is covered with snow. Snow melts and disappears from south slopes about a month before it does from north slopes (see graph). As spring a d van c e s, the snow disappear s progressively from the lower elevations to the higher. When one -half of the snow has disappeared, the spring peak in streamflow is approached; w hen 80 percent of the snow is gone the stream is declining in flow. 6 ~ !:1 ti4 UI ~ u °2 ~ o ~ o~--~~--~-----&----~----~----~ Apr5-12 Apr19-26 May3-IOMoy/7-24June 1-7 June 14-22 WEATHER FACTORS Temperature, humidity, and wind also influence the daily rate of snowmelt which. in turn. governs spring streamflow. Continuous records of these factors are useful in calculating rates of streamflow for the main St. Louis drainage. Cooperative studies with the Bureau of Reclamation have r.esulted in methods of forecasting daily streamflow. This diagram shows the relation-of snowcover disappearance to streamflow of St.Louis Creek _ Bare = One -third snow cover _ Two -thirds snow cover = Full snow cover C) 11.1 fO II: 11.1 Go ~ to. ~ C) I 11.1 CD II: C % C) ISO !!! ,.-' Q C Q ~ 11.1 ::I APRIL MAY JUNE PERIOD OF RECORD - - 14 - ~ULY APRIL 1 TO AUGUST SEPT. 30. 1960 SEPTEMBER Other investigations that bear on the :main proble:ms of water yields are tests of an overhead cable logging syste:m at the experi:mental forest and studies of alpine snowfields at Loveland Ski Basin. Both these studies round out efforts to increase water yields fro:m high-elevation forests and alpine areas. LOGGING METHODS WYSSEN A skyline -crane is being tested at the Fraser Experi:mental Forest to deter:mine its advantages in logging ti:mber on slopes too s te e p to log by tr ac to r s and horses and where w ate r she d values :must be protected. The essential parts of the skyline -crane are the yarder (winch and power plant) located at top of slope, the skyline, carriage, carriage stop, and inter:mediate supports. The installation and I 955 - 5 6 costs are shown here. SKYLINE CRANE LOGGING SUMMARY ISO M.B.F. OF COSTS/M 16 LOGS/M COSTS!M Stumpage $ 3.00 Falling 8. Bucking 6,60 Installation (2 settin9s) 7,90 Yarding 8. Skidding ~ Total f.o.b Landin9 $33.94 Hauling (8 miles) ~ Total f.o,b. Mill $39.44 Y.... RDiNG' SKiDDiNG CosTs/M Labor (incl. supervieion) $12.18 Gosoline 8. lubricants .26 Rese.ve suppl~ fund Depreciation Total 3.00 ~ TA-ILSPAR $16.44 Advantages of the skyline -crane are: 1. It can reach ti:mber that is nOW inaccessible. Roughly, one-third of the :mature ti:mber in Colorado and Wyo:ming cannot be logged by ordinary :methods because of steep slopes, excessive road-building costs, or possible da:mage to i:mportant watersheds. 2. Trees that :might otherwise be lost to insects, disease, decay, or old age can be salvaged and used. 3. Logging idle forest stands would increase the snowpack and subsequent water yield by opening up the canopy and letting :more snow reach the ground. 4. Since the skyline-crane eli:minates :most of the road building connected with logging, it would greatly reduce erosion. Trapping snow in natural catchment basins by artificial or natural barriers will enlarge alpine snowfields so that more water becomes available for late -summer streamflow. ALPINE SNOWFIELDS Alpine snowfields contribute to late-summer streamflow. Streamflow records of Middle Boulder Creek, 35.5 square miles in size, and Glacier Creek, 25.2 square miles in size, illustrate the contribution made by alpine snowfields to summer streamflow. The 1953 records show that Glacier Creek had a higher flow during August and September. Aerial photographs revealed 2.5 acres of alpine snow per square mile at the end of September in Glacier Creek drainage compared with 0.8 acre of alpine snow per square mile in Middle Boulder Creek. The facilities of the Fraser Experimental Forest are used from time to time for training schools, for undergraduate field work, for field meetings of forestry and conservation societies, and for the Foreign Agricultural S e r vic e program in forestry. Excellent examples, nearby and on the forest, serve as on-the-ground illustrations of both beneficial and harmful practices in mountain agriculture. Opportunities for graduate students to undertake fundamental research in the conservation and use of natural resources are excellent. Arrangements may be made through colleges, universities, foundations, or other interested groups, with the U. S. Forest Service, on a cooperative basis. VI~ITORS ARE ALWAYS WELCOME. To obtain more detailed published information about the experimental work, ask the resident technicians, or send a request to the D ire c tor, Rocky Mountain Forest and Range Experiment Station, Fort Collins, Colorado.